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 To understand the impact of dust deposition on ocean primary productivity, the evaluation of dust input is not sufficient, and the soluble iron supply is also needed. Measurements of iron in aerosols suggest a much higher solubility than in soil, implying substantial atmospheric processing of chemical or physical nature. Here, we have investigated the effect of the mineralogy on iron solubility. We have measured iron solubility from some minerals commonly found in dust (clay, feldspar and iron (hydr-)oxides). Firstly, we observe a greater solubility of iron resulting from clays (~4%) in comparison to iron (hydr-)oxides (<1%), independently of specific surface of minerals. Secondly, by considering amount of dissolved iron and the mineralogical composition of dust, our results indicate that dissolved iron fraction mainly comes from clay dissolution in contrast to that assumed in some biogeochemical models. In consequence, it appears that iron solubility is closely linked to the mineralogical composition of aerosol.
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 Studying iron solubility is important to understand the carbon biogeochemical cycle. Iron is an essential nutrient for marine microorganisms and is critical to ocean primary productivity. By influencing the pCO2 in the atmosphere, the carbon fixation by oceanic biota has a direct impact on Earth’s climate system (Wells et al., 1995). Atmospheric deposition, and the notably sporadic dust plume, was identified as the main iron supply, especially in remote oceans (Duce and Tindale, 1991). However, in order to consider the Fe impact on the ocean productivity, the key flux to the oceans is not dust, but soluble iron, which we assume here is the potentially bioavailable fraction. Soluble iron in soils represents about 0.5% of total iron, but measurements of iron in aerosols suggest a much higher solubility, implying substantial atmospheric processing [Jickells et al., 2005]. Indeed, solubility ranges from 0.01% to 80% and are highly heterogeneous in space and time [Mahowald et al., 2005]. Although it is clear that atmospheric processing changes the solubility of iron as it moves from the source regions to be deposited into oceans, the relative importance of the different mechanisms is not clear. On one hand, several studies have emphasized that photochemical reactions, organic complexation and cloud processes in the atmosphere can modify iron solubility of desert dust [Desboeufs et al., 2001; Chen and Siefert, 2004; Hand et al., 2004]. On the other hand, recent investigations, conducted by Baker and Jickells  suggest that dust iron solubility is rather controlled by particle size than by chemical processes during their atmospheric transport as a result of the increase of surface area to volume ratio of the dust population with distance away from desert source due to higher gravitational settling of largest particles. However, this size discrimination along the dust transport trajectory seems to have also an effect on the mineralogy of dust population. Several studies over Atlantic Ocean emphasize a change of the mineralogical composition of Saharan dust during their transport, with a decrease of quartz relative part in favour of clay fraction [Glaccum and Prospero, 1980]. These authors conclude that it is due to a much faster sedimentation of quartz. The size splitting up process occurring both at the emission and during atmospheric transport induces an increase of relative amount of fine particles and so an increase of relative clay content in dust plume. Over Pacific, Gao et al.  show also by dust deposition modeling that the clay fraction becomes more and more dominant downwind of the sources from Asia.
 In this paper, we present an estimation of iron solubility from pure minerals which compose dust aerosol under wet deposition conditions. The aim of this study was, firstly, to deduce the relationship between iron solubility and the mineralogical composition of dust particles and secondly to investigate a potential relationship between the iron solubility and the mineralogical splitting up that arise during atmospheric transport.
2. Materials and Method
2.1. Minerals Characterization
 Dust is mainly composed of a mixture of minerals such as clays, quartz and feldspars, but their relative contents are variable according to the collected area. Table 1 gives the mineralogical composition of African dust collected over Atlantic Ocean and Mediterranean. Among the clay group that represents between 48 and 82% of the total aerosol mass, illite and kaolinite are the dominant minerals. Smectite and chlorite are detected in most of samples but in very low concentrations. Among the non-clay minerals, quartz is the most common and ranges between 10 and 20%. Calcite and feldspars are always found in dust but in smallest proportions. Total iron content expressed as a percentage of the sample mass is around 4 to 7% depending on the source area. Iron in dust may be in the form of oxides (hematite, magnetite) and hydroxides (goethite) but is also present in aluminosillicate minerals. Lafon et al.  have measured the percentage of free-iron (iron in (hydr-)oxide) relative to the sample mass in dust aerosols: they found between 2.8 to 5% according to their origin and the free iron- to-the structural iron (iron trapped in the crystal lattice of aluminosilicates) ratio is often around 1.
Table 1. Mean Mineralogical Composition of African Dusta
 With these results in mind, we made the choice to study dissolution of most of the minerals present in dust that content iron, i.e. 2 feldspar, 3 iron (hydr-)oxide, 6 clay samples (Table 2). For each mineral, X fluorescence spectrometry analyses have been conducted to determine iron content and specific surface have been measure with the BET gas adsorption method [Fagerlund, 1973]. Results of the analysis and origin of the minerals are given in Table 2.
Table 2. Physical and Chemical Properties of Minerals Used
 10 mg of crushed mineral (particles < 100 μm), precisely weighed, was put into 250 ml of Milli-Q water acidified at pH 2 with nitric acid (NormatonTM), this acid is chosen because it is commonly found in rainwater [Li and Aneja, 1992]. After 60 min of contact time between acidified water and mineral particles with shaking, the solution was filtered through a 0.2 μm polycarbonate filter. Dissolved iron concentration (DFe) in the filtered sample was analyzed by GFAAS (ATI-Unicam 929) [Sofikitis, 2004]. Multi-elementary analysis of the dissolved phase was made by ICP-AES (PE Optima 3000) [Desboeufs et al., 1999]. All handling was performed in an ultra clean laboratory (class < 1000) under ultra clean laminar flow benches (class < 10). The iron solubility (%FeS) is calculated as follows: %FeS = 100 × (DFe/Fetot) where Fetot is the total mineral concentration of iron. Preliminary studies, carried out in atmospheric conditions (pH 4.7 and loading charge = 10 mg/L), showed that dissolved concentrations were close to the detection limit of the analytical methods when measuring the solubility of (hydr-)oxides [Sofikitis, 2004]. Knowing that low pH increases iron solubility [Desboeufs et al., 1999], we adjust the pH of the aqueous phase to 2 to obtain enough iron to be above our detection limit. The particulate loading was fixed to 40mg/L. The ratio of the iron solubility between oxides and clays measured at pH 4.7 is approximately 2 orders of magnitude lower than the ratio at pH 2 [Sofikitis, 2004]. Thus, in this work, iron solubility in natural waters will be overestimated, and not necessarily in a linear fashion, meaning that the relationship between solubility at pH 4.7 and pH 2 is not linear. Thus, in this work, iron solubility could be overestimated for oxides.
3. Results and Discussion
 The results, presented in Table 3, emphasize that the solubility of iron (hydr-)oxides is much lower than for aluminosilicate minerals. Thus it appears that the iron (hydr-)oxides which are the richest in iron, release the least iron into water in comparison with the clays or the feldspars. In order to consider if iron solubility is related to the Fetot in the minerals, %FeS versus Fetot for each mineral is plotted in Figure 1. Figure 1 emphasizes an exponential decrease of iron solubility with the mineral iron content increase. This trend has been already observed by Zhuang et al.  for aerosol samples collected over Pacific Ocean. These authors have suggested that iron chemical form in aerosol, i.e. (i) iron in aluminosilicate phase and (ii) iron in hydroxide phase, could be an explanation of this trend. Moreover, the low dissolution rate of hydrous oxides in comparison with aluminiosilicates is well known in aquatic surface geochemistry [Stumm and Furrer, 1987]. Most of the dissolution reactions of minerals are critically dependent on the coordinative interactions taking place on surface [Wieland et al., 1988]. In consequence, the exponential trend of iron solubility could be linked to the type of chemical bonds in which iron atoms are implied in the mineral, Fetot being a simple tracer of type of bonding. To investigate the role of the type of bond, dissolved iron concentrations have been compared to other dissolved elements (X = Al, K or Mg). A ratio (DX/DFe)/(Xtot/Fetot) which is close to 1 shows that the Fe and X are dissolved according to a similar dissolution process, while a ratio < or > 1 emphasizes a preferential dissolution for Fe or X respectively. On this calculation basis, 4 types of dissolved iron behaviour can be distinguished (Figure 1 and Table 3):
Table 3. Solubility, Specific Surface Effect, and Comparison Between Dissolved Fraction of Iron and Other Elements (Al, K and Mg)
%Fes/SS, % m−2 g1
Dissolved fraction under detection limit of ICP-AES.
 1. Iron (hydr-)oxides are composed by Fe, H and O (Case A). In these minerals, iron is inferred to be in the strong Fe-O lattice bonds.
 2. The case of nontronite and beidellite (Case B) for which Fe dissolution presents a comparable behaviour to Al. Indeed, for these minerals, iron is known to be generally in substitution of this element in the crystalline network [Deer et al., 1966]. Thus, Fe is located in the octahedral (Al-bearing) or tetrahedral (Si-bearing) layers bound by covalent bonds.
 3. The minerals where Fe is dissolved in an identical pattern to K or Mg (e.g. orthoclase, illites and montmorillonite (case C)), where Fe substitutes for Mg or K In this case, ionic bonds hold Fe in the lattice.
 4. In the minerals where Fe is in the form of impurities such as kaolinite and oligoclase, no relationship of Fe dissolution with others elements is observed. (Case D). Mermut and Cano  provide chemical analyses of the kaolinite KGa1 and show that the Fe content corresponds to a contamination by amorphous free iron impurities.
 The solubility is the highest for the minerals where the Fe is probably found as amorphous impurities and the lowest for the (hydr-)oxides where iron is bound by covalent bonds in the crystalline lattice (Figure 1). For the intermediate solubility values, %FeS< 1% if it substitutes Si and Al in the lattice and > 1% if it replaces alkaline elements as interlayer ions.
Baker and Jickells  claim recently changes in the mean surface area to volume ratio of the mineral aerosols population, caused by progressive removal of larger particles during transport, account for the trend in aerosol Fe solubility. As mineral particles become smaller, a greater proportion of their volume is exposed and therefore available for dissolution. Such phenomenon is known in the geochemical area as surface-controlled dissolution [Stumm and Furrer, 1987]. In order to consider the specific surface effect, specific surfaces (SS) have been compared to the iron solubility by determining the ratio %FeS/SS (Table 3). No relationship is observed between iron solubility and specific surface. The ratio %FeS/SS is under 0,005% .m−2.g for iron (hydr-)oxide while for clays it is at least twice much higher, that means the great difference in iron solubility between these two mineral classes is not linked with the specific surface. Globally, specific surface effect on iron solubility doesn’t seem to be as much significant as the chemical structure of solid phase. In consequence, it appears that iron solubility is closely linked to the mineralogical composition of aerosol.
4. Biogeochemical Implications
 As iron oxides and hydroxides are composed by more than 50% of iron, they are usually considered as the main suppliers of dissolved iron resulting from dust particles dissolution. For example, several models predicting atmospheric dust deposition of soluble iron in ocean assume that soluble Fe within the dust mode is produced primarily through the dissolution of hematite [Meskhidze et al., 2003; Fan et al., 2006]. Our work allows us to check this hypothesis by calculating the contribution of each mineral found in dust to the total dissolved iron. Under the specific condition of this study, the concentration of dissolved iron coming from dust dissolution was estimated for an average mineralogical composition that was calculated using the mean values of the mineralogical composition from Table 1 (see Table 4). The relative mass content of iron (hydr-) oxides in dust is estimated with the dataset from Lafon et al. . For each mineral, concentrations of dissolved iron were calculated from their iron solubility values multiplied by their relative iron fraction in dust aerosols. Thus, the contribution of each mineral to the total dissolved iron is summarized in Table 4. These results point out the large contribution of clays, which represents more than 96% of the total dissolved iron, despite their low iron content but thanks to their high iron solubility. On the other hand, the input from (hydr)oxides dissolution is quasi-negligible. Literature shows that reactions of ferric iron from oxides with organic species such as oxalate or by photochemical processes could play a significant role in producing soluble iron (e.g., Siffert and Sulzberger, 1991). Siffert and Sulzberger  show that iron solubility in presence of oxalate increases by a factor 10 upon irradiation. However, even in these favourable conditions, iron solubility could reach value around 0.5% that is always smaller than the iron solubility of clays. Our results therefore suggest that the use of iron (hydr)oxides and particularly hematite in biogeochemical models, might induce an underestimation of the dissolved iron supply and hence an overestimation of atmospheric chemical processes contribution as in the increase of the solubility during dust transport. The impact of this trend in Fe solubility will be to smooth out the strong gradients in atmospheric iron supply to the ocean, with proportionately less soluble Fe delivered to areas close to major dust sources and more to remote areas, relative to most current models, which use a fixed value for aerosol Fe solubility. To provide realistic iron solubility values from mineral dust in wet deposition to the biogeochemical models, future work is planned in close conditions of a rainwater composition (pH, organic ligands) on each mineral. Moreover, the high solubilities observed in dust aerosols [Mahowald et al., 2005] cannot be simply explained from our results; the contribution of the atmospheric processing or others sources of soluble iron need to be evaluated. Atmospheric process acting on mineralogical composition may produce more soluble matter. In consequence, further dissolution experiments on dust with various mineralogical compositions collected in source areas and after transport are indispensable to distinguish the effect of dust origin mineralogy and atmospheric processing. Finally, this work suggests that it is necessary to follow the mineralogy in the atmosphere, and its evolution with transport, in order to parameterize iron solubility in models.
Table 4. Experimental Estimation of Iron Solubility and Contribution of Each Mineral Group to Total Dissolved Iron